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APPENDIX A Evaluate whether a release has transpired:One of the circumstances where passive <br /> PASSIVE SOIL GAS METHOD methods are effective in collecting soil gas samples are in areas with low <br /> permeability and high moisture setting(Le.,soil in areas with shallow groundwater <br /> Both passive and active soil gas sampling and analyses may need to be performed to due to high water table)where active soil gas samples are more difficult to obtain. <br /> provide multiple lines of evidence to evaluate vapor intrusion exposure to organic When the depth to groundwater is shallow(i.e.,within 5 it bgs),the capillary fringe <br /> vapors. Passive soil gas sampling is a qualitative method,which consists of the burial may prevent sample collection by conventional active methods due to moisture <br /> preventing soil gas Flow into the probe. Passive soil gas methods can be used to <br /> of an adsorbent material into the subsurface soil with subsequent retrieval and <br /> determine whether or not volatile compounds have contaminated the soil of current <br /> measurement of organic vapors passively amassed onto the absorbent material. Unlike <br /> as from or historic industrial operations along coastal areas with a high water table or to <br /> active soil gas sampling,which consists of the physical withdrawal of the soil <br /> 9 determine whethernot naphthalene is present in soil gas. Sampling for <br /> the subsurface,with passive sampling,there is no forced movement of soil gas into the naphthalene by active methods may be difficult due to absorption or plating of <br /> sampling vessel. Instead,as the vapors migrate,the sorbent acts as a sink for the naphthalene onto the tubing and collecting vessels. • <br /> volatile organic compounds(VOCs)and semi-volatile organic compounds(SVOCs) <br /> found in soil gas. Additional advantages over active soil gas methods: <br /> Passive soil gas methods measure a mass(e.g.micrograms)of contaminant that has <br /> 1. Passive soil gas methods give a time-integrated measurement,and therefore, <br /> diffused onto an adsorbent media. Unlike active soil gas methods which yield reduce the uncertainty due to temporal variations. <br /> concentration data(e.g., ug/m'or uglL)that can directly be compared to risk-based <br /> screening levels or used in predictive models,passive soil gas methods do not generate 2. Passive soil gas methods are frequently capable of detecting and reporting <br /> contaminant concentration data. While there are published methods and procedures to <br /> generate concentration data from a passive sorbent-based sampler in ambient air,there compounds present at very low levels not detected by active methods, <br /> are no published studies demonstrating the.applicability of this method to soil gas. This 3. Simplicity of installation and retrieval: Unlike the active sampling method which <br /> is because the gas-phase diffusivity in the vadose zone is unknown for the calculation of <br /> of <br /> a concentration from the adsorbed mass. There are a limited number of field studies involves withdrawal is no forced movemenn the soil gas(forced extraction)from the subsurface,there <br /> that attempt to calibrate the mass of contaminant collected by passive method to actual t of soil gas into the sampling vessel with passive methods. <br /> soil gas concentrations and for derivation of a method for this conversion. For this Therefore,the seal integrity of the vapor probe does not need to be ensured as in <br /> reason,passive soil gas sampling and analysis is presently not considered to be the case of the active method. - <br /> applicable as a stand-alone method for determination of vapor intrusion risk. Provide Additional Line of Evidengg for Vapor Intrusion Attribution of chemicals in <br /> Although passive soil gas methods do not provide contaminant concentration data for indoor air to vapor intrusion can be a complex and difficult task. Therefore.itis <br /> important to use multiple lines of evidence to reach decisions based on professional <br /> use in predictive modeling and therefore is considered to be a qualitative tool,this judgment. In this regard,alternative sampling methods,in addition to the active soil gas <br /> method does have applications in plume characterization and vapor intrusion sampling procedures may.:be employed especially in certain circumstances as <br /> assessments. Potential uses and advantages of this method are as follows: described above. All available data from the multiple lines of evidence collected during <br /> • <br /> Locate contaminant hot soots for later sampling and plume characterization: Passive the investigation(active and passive)should be used in determining whether vapor • <br /> soil gas can be a viable,cost-effective and simple screening tool to determine areas intrusion Is occurring and whether there are potential public health concerns. <br /> of contamination. The location of sources and subsurface plumes can be mapped, Attempts should be made to collect active soil gas data from specific locations after the <br /> particularly edges of plumes to determine whether contamination is near existing or presence and composition of subsurface chemical constituents in the vadose zone has <br /> future buildings. been established by the passive method. Active soil gas sample collection from areas <br /> • and inexpensive means with tighter lithology or in areas with shallow groundwater may need to be collected <br /> Locate preferentialpathways:Passive methods offer a quick q P using a vacuum of less than 100-inches of water column at a rate less than or equal to <br /> to find vapor migration pathways into and around buildings and other sub-surface 100 mUmin using canisters to provide a more representative sample(McAlary at at, <br /> structures such as sewer and utility corridors. Other preferential pathways for 2009). <br /> migration such as geological features including potential spatial variability in the <br /> lithology can be identified by use of the passive sampling technique. <br /> 12/10/2009 -49- 12/10/2009 <br /> -50- <br />